环境科学
植物凋落物
微生物种群生物学
土壤有机质
土壤水分
有机质
垃圾箱
温带森林
固碳
温带气候
生物量(生态学)
土壤碳
分解
环境化学
土壤科学
森林地面
农学
土壤生物学
温带雨林
生态学
碳纤维
化学
溶解有机碳
生态系统
总有机碳
碳循环
微生物
生物地球化学循环
大块土
土壤化学
土工试验
作者
Isla Wrightson,Meiling MAN,Laura Castañeda‐Gómez,Nivetha Srikanthan,Huan Tong,Melissa A. Knorr,Serita D. Frey,Knute J. Nadelhoffer,Kate Lajtha,Myrna J. Simpson
标识
DOI:10.1021/acs.est.5c11996
摘要
The capacity of forest soils to sequester carbon (C) is susceptible to shifts in the litter quantity and chemistry. Using measurements from the third decade of a long-term Detrital Input and Removal Treatment (DIRT) experiment at Harvard Forest (MA, USA), extending previously published work from 20 years, we examined how litter inputs shape soil organic matter (SOM) chemistry. Elemental analysis, targeted compound analysis, solid-state 13C nuclear magnetic resonance (NMR) spectroscopy, and microbial biomass and community composition measurements were used. Despite doubled litter inputs over 30 years, no net soil C accumulation occurred, and the SOM decomposition stage was similar to the control, suggesting continuous microbial processing of added inputs. The exclusion of litter, roots, or both led to lower soil C and more advanced SOM decomposition in mineral soils. Shifts in microbial community composition, particularly an increase in Gram (+) to Gram (-) bacteria under exclusion treatments, point to microbial reorganization in response to altered substrate availability. This long-term study underscores the limited potential for long-term soil C sequestration due to sustained microbial decomposition and the role of continuous plant inputs in shaping SOM chemisty under changing detrital regimes in a temperate forest.
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